Described are apparatuses, systems, and methods for treating exhaust. The described apparatus and systems typically include a catalytic device for converting aqueous urea to ammonia. The catalytic device may include a pyrolysis catalyst and a hydrolysis catalyst for converting aqueous urea to ammonia. The catalytic device typically includes an upstream face that is positioned at an angle relative to exhaust flow when the device is positioned in a selective catalytic reduction (SCR) system.

Patent
   8071037
Priority
Jun 25 2008
Filed
Jun 25 2008
Issued
Dec 06 2011
Expiry
Jul 02 2030
Extension
737 days
Assg.orig
Entity
Large
8
185
all paid
15. A permeable catalytic device for converting urea to ammonia comprising a separate first portion and a separate second portion, and the first portion comprises a pyrolysis catalyst and the second portion comprises a hydrolysis catalyst, wherein the first portion and the second portion are positioned adjacent to each other to form the catalytic device, and the catalytic device is one of parallelogram-shaped in cross-section and trapezoid-shaped in cross-section.
17. A method of manufacturing a permeable catalytic device for converting urea to ammonia, the device comprising a pyrolysis catalyst and a hydrolysis catalyst, the method comprising:
(a) manufacturing a first portion of the device, wherein the first portion comprises the pyrolysis catalyst and has an upstream face and a downstream face;
(b) manufacturing a second portion of the device, wherein the second portion comprises the hydrolysis catalyst and has an upstream face and a downstream face; and
(c) positioning the downstream face of the first portion adjacent to the upstream face of the second portion, thereby forming the device;
wherein the manufactured device is parallelogram-shaped in cross-section or trapezoid-shaped in cross-section.
13. A method of manufacturing an apparatus for treating exhaust comprising:
(a) providing a housing having an upstream inlet for receiving the exhaust, and a downstream outlet for discharging the exhaust, the housing defining an axial flow path for the exhaust;
(b) positioning in the housing an injector for injecting a urea solution into the exhaust; and
(c) positioning downstream of the injector a catalytic device for converting urea to ammonia, the catalytic device having an upstream face that is positioned at an angle of about 20-70 degrees relative to the axial flow path, and the catalytic device configured to receive the urea solution from the injector at the upstream face;
wherein the catalytic device is parallelogram-shaped in cross-section or trapezoid-shaped in cross-section.
1. An apparatus for treating exhaust comprising:
(a) a housing having an upstream inlet for receiving the exhaust, and a downstream outlet for discharging the exhaust, the housing defining an axial flow path for the exhaust;
(b) an injector configured to inject a urea solution into the exhaust;
(c) a permeable catalytic device for converting urea to ammonia positioned in the axial flow path downstream of the injector, wherein the catalytic device has an upstream face that is positioned at an angle of about 20-70 degrees relative to the axial flow path and the catalytic device is configured to receive the urea solution from the injector at the upstream face; and
(d) a selective catalytic reactor for converting NOx to nitrogen gas and water in the presence of ammonia, wherein the selective catalytic reactor is positioned downstream of the catalytic device;
wherein the catalytic device is parallelogram-shaped in cross-section or trapezoid-shaped in cross-section.
2. The apparatus of claim 1, wherein the upstream face is positioned at an angle of about 30-50 degrees relative to the axial flow path.
3. The apparatus of claim 1, wherein the catalytic device has a downstream face that is positioned at a right angle relative to the axial flow path.
4. The apparatus of claim 1, wherein the catalytic device is trapezoid-shaped in cross-section.
5. The apparatus of claim 1, wherein the injector is positioned at an angle of about 20-70 degrees relative to the axial flow path.
6. The apparatus of claim 1, wherein the injector is positioned at an angle of about 90±15 degrees relative to the upstream face of the catalytic device.
7. The apparatus of claim 1, wherein the catalytic device comprises a pyrolysis catalyst.
8. The apparatus of claim 1, wherein the catalytic device comprises a hydrolysis catalyst.
9. The apparatus of claim 1, wherein the catalytic device comprises a pyrolysis catalyst and a hydrolysis catalyst.
10. The apparatus of claim 1, wherein the catalytic device comprises an upstream portion and a downstream portion, and the upstream portion comprises a pyrolysis catalyst and the downstream portion comprises a hydrolysis catalyst.
11. The apparatus of claim 10, wherein the upstream portion and the downstream portion are separate.
12. A method for treating exhaust comprising passing exhaust through the apparatus of claim 1.
14. The method of claim 13, further comprising:
(d) positioning downstream of the catalytic device a selective catalytic reactor for converting NOx to nitrogen gas and water in the presence of ammonia.
16. An apparatus for treating exhaust comprising:
(a) a housing having an upstream inlet for receiving the exhaust, and a downstream outlet for discharging the exhaust, the housing defining an axial flow path for the exhaust;
(b) an injector configured to inject a urea solution into the exhaust;
(c) the catalytic device of claim 15 positioned downstream of the injector; and
(d) a selective catalytic reactor for converting NOx to nitrogen gas and water in the presence of ammonia, the selective catalytic reactor positioned downstream of the catalytic device for converting urea to ammonia.
18. The method of claim 17, further comprising coupling the first portion and the second portion.

The field of the invention relates to exhaust aftertreatment devices for internal combustion engines. In particular, the field of the invention relates to selective catalytic reduction (SCR) systems for internal combustion engine exhaust including those suitable for use in industrial processes and in mobile and stationary diesel, natural gas, and other engine applications.

Exhaust from internal combustions engines typically includes oxidized nitrogen gases such as nitrogen oxide (NO), nitrogen dioxide (NO2), and nitrous oxide (N2O), which collectively are referred to as “NOx.” Because NOx can be an environmental hazard, systems have been developed to remove NOx from exhaust by selective catalytic reduction (SCR).

Selective catalytic reduction (SCR) of nitrogen oxides (NOx) using a reducing agent is known in industrial processes as well as in stationary diesel engine applications. Ammonia is a commonly used reducing agent in SCR systems. NOx reacts with ammonia and is catalytically reduced by a SCR to nitrogen gas (N2) with water as a by-product. This reaction may be represented generally as follows:
NOx+NH3→N2+H2O
This reaction may be catalyzed by catalysts referred to as “SCR catalysts.”

Because ammonia is a hazardous substance, typically ammonia is not directly introduced into SCR systems. Rather, ammonia is generated in situ by introducing a less hazardous, ammonia-generating source into the SCR system. One common ammonia-generating source is aqueous urea. In the SCR system, aqueous urea is injected into the exhaust gas flow stream upstream of the SCR. Water in the droplets from the injection solution evaporate leaving urea, which decomposes in heat (i.e., pyrolyzes) to isocyanic acid and ammonia. In water, isocyanic acid then hydrolyzes to create ammonia and carbon dioxide. These reactions may be represented generally as follows:
CO(NH2)2+heat→HNCO+NH3
HNCO+H2O→NH3+CO2
These reactions may be catalyzed by catalysts referred to as “pyrolysis catalysts” and “hydrolysis catalysts,” respectively. The ammonia thus formed may react and reduce NOx in a SCR reaction.

The use of SCR catalysts for mobile applications is problematic. One obstacle is that mobile applications are relatively small in size. This makes it difficult to inject a urea solution into exhaust upstream of an SCR catalyst and decompose and hydrolyze the urea solution completely to ammonia prior to the exhaust arriving at the SCR catalyst (and achieve a high enough ratio of ammonia to NOx). At low diesel engine exhaust temperatures and high gas flow velocities (e.g., about 20 meters per second), a distance of several meters (i.e., a time of 0.1 to 0.3 seconds) between the injector and the SCR catalyst is required for the aqueous urea solution spray to vaporize, for urea to decompose and hydrolyze into ammonia and carbon dioxide, and for the ammonia to become practical uniformly distributed across the flow front before entering the catalyst. Although various solutions to this problem have been suggested, (see, e.g., U.S. Pat. Nos. 6,928,807; 6,361,754; and 6,203,770; and U.S. published application No. 2006/0115402), these solutions involve generating ammonia outside of the SCR system and introducing the ammonia directly into the exhaust stream. In these systems, if the SCR catalyst is not pre-heated prior to introduction of this ammonia, the ammonia will pass through the SCR catalyst and foul the air. Therefore, there is a need for improved SCR systems that are suitable for mobile applications.

Disclosed are apparatuses, systems, and methods for treating exhaust. The disclosed apparatuses, systems, and methods typically include or utilize a catalytic device for converting an aqueous urea solution to ammonia.

The disclosed apparatuses and systems for treating exhaust may include a housing having an upstream inlet for receiving the exhaust, and a downstream outlet for discharging the exhaust, where the housing defines an axial flow path for the exhaust. The disclosed apparatuses and systems further may include an injector configured to inject a urea solution into the exhaust. The disclosed apparatuses and systems typically include a catalytic device for converting urea to ammonia, which is positioned in the axial flow path downstream of the injector (e.g., a permeable catalytic device). The catalytic device has an upstream face that is positioned at an angle relative to the axial flow path (e.g., at an angle of about 20-70 degrees relative to the axial flow path, preferably at an angle of about 30-50 degrees relative to the axial flow path). The catalytic device typically is configured to receive the urea solution from the injector at the upstream face. The disclosed apparatuses and systems further may include a selective catalytic reactor (SCR) for converting NOx to nitrogen gas and water in the presence of ammonia, where the SCR is positioned downstream of the disclosed catalytic device.

Also disclosed are methods of manufacturing the disclosed apparatuses and systems. The methods may include methods for manufacturing an apparatus for treating exhaust. The methods may include: (a) providing a housing having an upstream inlet for receiving the exhaust, and a downstream outlet for discharging the exhaust, where the housing defines an axial flow path for the exhaust; (b) positioning in the housing an injector for injecting a urea solution into the exhaust; and (c) positioning downstream of the injector a catalytic device for converting urea to ammonia. Typically, the catalytic device has an upstream face that is positioned at an angle relative to the axial flow path (e.g., at an angle of about 20-70 degrees relative to the flow path, or preferably at an angle of about 30-50 degrees relative to the flow path). Typically, the catalytic device is configured to receive the urea solution from the injector at the upstream face. Optionally, the methods may include: (d) positioning downstream of the catalytic device a selective catalytic reactor for converting NOx to nitrogen gas and water in the presence of ammonia.

The disclosed methods may include methods for manufacturing a permeable catalytic device for converting urea to ammonia, where the device includes a pyrolysis catalyst, a hydrolysis catalyst, or both. The method for manufacturing the device may include: (a) manufacturing a first portion of the device, where the first portion includes the pyrolysis catalyst and has an upstream face and a downstream face; (b) manufacturing a second portion of the device, where the second portion includes the hydrolysis catalyst and has an upstream face and a downstream face; and (c) positioning the downstream face of the first portion adjacent to the upstream face of the second portion, thereby manufacturing the device; where the manufactured device is parallelogram-shaped in cross-section or trapezoid-shaped in cross-section. Optionally, the method for manufacturing the device further may include coupling the first portion and the second portion.

Also disclosed are methods of treating exhaust that utilize the disclosed apparatuses and systems. In some embodiments, the methods include passing exhaust through the disclosed catalytic devices, where the devices comprise a pyrolysis catalyst, a hydrolysis catalyst, or both. The exhaust may passively heat the catalytic device and promotes conversion of aqueous urea to ammonia, where aqueous urea is injected into the exhaust flow and deposited on an upstream face of the catalytic device.

The disclosed apparatuses and systems utilize a catalyst device for converting urea to ammonia. In some embodiments, the required distance between the injector and the catalytic device in a SCR system for achieving complete conversion of urea to ammonia is reduced by utilizing the disclosed catalytic device. The disclosed SCR systems may be suitable for mobile applications.

FIG. 1 shows an SCR system for exhaust of the prior art.

FIG. 2 is a sectional view of one embodiment of an SCR system as disclosed herein.

FIG. 3 is a sectional view of another embodiment of an SCR system as disclosed herein.

FIG. 4 provides sectional views of four embodiments (A, B, C, and D) of a catalytic device as disclosed herein.

FIG. 5 provides a sectional view of a portion of one embodiment of an SCR system as disclosed herein.

FIG. 6 provides a sectional view of a portion of another embodiment of an SCR system as disclosed herein.

FIG. 7 provides a perspective view of one embodiment of a catalytic device as disclosed herein.

Disclosed are apparatuses, systems, and methods for treating exhaust. The disclosed apparatuses, systems, and methods typically include or utilize a catalytic device for converting an aqueous urea solution to ammonia. The catalytic device may include a pyrolysis catalyst, a hydrolysis catalyst, or both. The catalytic device typically has an upstream face that is positioned at an angle relative to an axial exhaust flow when the device is positioned in an SCR system. The upstream face typically is positioned to receive an aqueous urea solution that is injected from a nozzle of a urea tank.

The disclosed apparatuses and systems typically include a catalytic device having an upstream face that is positioned at an angle relative to an axial flow path. The disclosed apparatuses and systems may include a catalytic device having a downstream face that is positioned at a right angle relative to an axial flow path or at an angle of 90 degrees (±15 degrees) relative to the axial flow path, for example, if flow distribution uniformity is not a concern and the same length of exhaust gas pathlines is not required. In some embodiments, the disclosed apparatuses and systems may include a catalytic device having a downstream face that is positioned at an angle of about 20-70 degrees relative to the axial flow path, or at an angle of about 30-50 degrees relative to the axial flow path). In further embodiments, the upstream face and the downstream face of the catalytic device are positioned at about the same angle relative to the axial flow path. Because the catalytic device has an upstream face that is positioned at an angle relative to the axial flow path, the catalytic device typically is not square-shaped or rectangular-shaped in cross-section. In some embodiments, the catalytic device is trapezoid-shaped in cross-section or parallelogram-shaped in cross-section.

In the disclosed apparatuses and systems, the injector may be positioned at an angle that is not parallel or perpendicular to the axial flow path. In some embodiments, the injector is positioned at an angle of about 20-70 degrees relative to the axial flow path (preferably at an angle of about 30-50 degrees relative to the axial flow path). In further embodiments, the injector may be positioned at an angle of about 90 degrees (±15 degrees) relative to the upstream face of the catalytic device.

The catalytic device catalyzes the conversion of aqueous urea to ammonia. The catalytic device may include a pyrolysis catalyst, a hydrolysis catalyst, or both (preferably both). The device may be monolithic (i.e., composed of single piece of material), or segmented (i.e., composed of two or more separate pieces of material which optionally are coupled together). In some embodiments, the catalytic device is composed of a pyrolysis catalyst and is coated with a hydrolysis catalyst.

The catalytic device may include an upstream portion and a downstream portion, where the upstream portion includes a pyrolysis catalyst and the downstream portion includes a hydrolysis catalyst. The upstream portion and the downstream portion may be separate portions that are placed adjacently and optionally may be coupled. In some embodiments, the upstream portion and the downstream portion are separate portions that are parallelogram-shaped in cross-section. In further embodiments, the upstream portion and the downstream portion are separate portions that are triangular-shaped in cross-section, trapezoid-shaped in cross-section, square-shaped in cross-section, or rectangle-shaped in cross-section and are placed adjacently to provide a catalytic device that is trapezoid-shaped in cross-section or parallelogram-shaped in cross-section.

The catalytic device may comprise a material, including but not limited to: extruded material; wrapped material (e.g., pleated or corrugated material); and layered material. The catalytic device preferably comprises a material selected from a group consisting of extruded monolith material; composite ceramic material, (e.g., as in U.S. Pat. Nos. 6,582,490; and 6,444,006, which are incorporated by reference herein in their entireties); fibrous material; and metallic material, (e.g., flow-through metal foils and the like). Preferably, the catalytic device is permeable or porous. In the disclosed apparatuses and systems, the catalytic device may be heated by exhaust (e.g., passively to a temperature of at least about 200° C. or about 200-700° C. or about 200-300° C.) or by a heat source (e.g., actively by an electronic heat source) to accelerate evaporation and decomposition and enhance hydrolysis or urea to ammonia.

The catalytic devices may include a pyrolysis catalyst, a hydrolysis catalyst, or both (preferably both) for converting urea to ammonia. The catalytic device may be manufactured from material that functions as a pyrolysis catalyst, a hydrolysis catalyst, or both. In some embodiments, the catalytic device is coated with a material that functions as a pyrolysis catalyst, a hydrolysis catalyst, or both.

The pyrolysis catalyst comprises a material that catalyzes the conversion of urea to ammonia (or to isocyanic acid) in the presence of heat (e.g., at a temperature of at least about 200° C.). Suitable pyrolysis catalysts may include, but are not limited to, materials having a relative high heat capacity such as metals or metal alloys. Suitable metals and metal alloys may include, but are not limited to iron or iron alloys (e.g., stainless steel), aluminum or aluminum alloys, and copper or copper alloys. In some embodiments, a pyrolysis catalyst may be coated with a different pyrolysis catalyst or a hydrolysis catalyst. The hydrolysis catalyst comprises a material that catalyzes the conversion of urea to ammonia in the presence of water (or the conversion of isocyanic acid to ammonia in the presence of water). Suitable hydrolysis catalysts may include, but are not limited to, metals and metal oxides (e.g., transition metals or transition metal oxides such as titanium, palladium, platinum, vanadium, chromium, molybdenum, nickel, or oxides thereof).

The disclosed apparatuses and systems typically include a catalytic device for converting aqueous urea to ammonia. The disclosed apparatuses and systems also may include a SCR catalyst. The SCR catalyst comprises, or is coated or impregnated with, a material that catalyzes the conversion of NOx to nitrogen gas and water. SCR catalysts may include, but are not limited to, activated carbon, charcoal or coke, zeolites, vanadium oxide, tungsten oxide, titanium oxide, iron oxide, copper oxide, manganese oxide, chromium oxide, noble metals such as platinum group metals like platinum, palladium, rhodium, and iridium, and combinations thereof.

The catalysts disclosed herein, including the pyrolysis catalysts, hydrolysis catalysts, and SCR catalysts may comprise a support material or may be mounted on a support material. Support material may include, but is not limited to, ceramic substances, zeolites, homogeneous monolith materials, and metals and metal alloys. The disclosed catalytic devices may be utilized in SCR exhaust aftertreatment systems. SCR systems are disclosed in U.S. Pat. Nos. 6,449,947; 6,601,385; 6,722,123; and 7,328,572, the contents of which are incorporated herein in their entireties.

Referring now to the drawings, FIG. 1 shows an SCR system for exhaust of the prior art. Exhaust is emitted from engine 62. Pump 64 draws aqueous urea solution from tank 26 and supplies same through valve 66 which is controlled by controller 68 which in turn is controlled by the engine. Engine exhaust is initially supplied through pre-oxidation catalyst 70 and then mixed with the aqueous urea solution injected at 72 into exhaust pipe 74. The mixture then flows downstream to hydrolysis catalyst 76, SCR catalyst 28 and oxidation catalyst 30. Housing 10 has a given cross-sectional area at SCR catalyst 28 transverse to axial flow 48 of exhaust.

FIG. 2 is a sectional view of one embodiment of an SCR system as disclosed herein. Exhaust enters the system along an axial flow path 148. A urea tank 102 injects an aqueous urea solution 104 through an injector 106. The aqueous urea solution is deposited on the upstream face 108 of a permeable catalytic device 111 that is trapezoid-shaped. The catalytic device comprises a pyrolysis catalyst and a hydrolysis catalyst. Exhaust heats the catalytic device and the aqueous urea solution is evaporated and heated to catalyze the conversion of urea to ammonia (or isocyanic acid, which is subsequently converted to ammonia). The exhaust exits the catalytic device at a downstream face 114. The exhaust passes through an SCR catalyst 116 and an exhaust catalyst 118 prior to exiting the system.

FIG. 3 is a sectional view of another embodiment of an SCR system as disclosed herein. Exhaust enters the system along an axial flow path 248. A urea tank 202 injects an aqueous urea solution 204 through an injector 206. The aqueous urea solution is deposited on the upstream face 208 of a catalytic device that comprises a permeable pyrolysis catalyst 210 and a permeable hydrolysis catalyst 212. Exhaust heats the pyrolysis catalyst and the aqueous urea solution is evaporated and heated to catalyze the conversion of urea to ammonia (or isocyanic acid, which is subsequently converted to ammonia). The exhaust passes through the pyrolysis catalyst 210 to the hydrolysis catalyst 212. The hydrolysis catalyst comprises, or is coated or impregnated with, an agent that catalyzes the hydrolysis of urea (or isocyanic acid) to ammonia. The exhaust exits the hydrolysis catalyst at a downstream face 214. The exhaust passes through an SCR catalyst 216 and an exhaust catalyst 218 prior to exiting the system.

FIG. 4 provides sectional views of three embodiments (A, B, C, and D) of a catalytic device as disclosed herein. In FIG. 4A, the catalytic device 302 is monolithic and trapezoid-shaped in cross-section. The device includes an upstream face 304 configured for receiving an aqueous solution of urea and configured to receive exhaust when the device is placed in an SCR system. The device includes a downstream face 306 that is configured such that exhaust exits the downstream face when the device is placed in an SCR system. FIG. 4B illustrates a catalytic device that is parallelogram-shaped in cross-section and includes a separate pyrolysis catalyst 312 that is trapezoid-shaped in cross-section and a separate hydrolysis catalyst 314 that is trapezoid-shaped in cross-section. The pyrolysis catalyst 312 and the hydrolysis catalyst 314 are positioned adjacently where a downstream face 318 of the pyrolysis catalyst is adjacent to an upstream face 320 of the hydrolysis catalyst to form the catalytic device. When the device is placed in an SCR system, the upstream face of the pyrolysis catalyst 316 is configured to receive an aqueous solution of urea and is configured to receive exhaust. When the device is place in an SCR system, the downstream face of the hydrolysis catalyst 322 is configured such that exhaust exits the downstream face. FIG. 4C illustrates a catalytic device that is parallelogram-shaped in cross-section and includes a separate pyrolysis catalyst 332 that is parallelogram-shaped in cross-section and a separate hydrolysis catalyst 334 that is parallelogram-shaped in cross-section. The pyrolysis catalyst 332 and the hydrolysis catalyst 334 are positioned adjacently where a downstream face 338 of the pyrolysis catalyst is adjacent to an upstream face 340 of the hydrolysis catalyst to form the catalytic device. When the device is placed in an SCR system, the upstream face of the pyrolysis catalyst 336 is configured to receive an aqueous solution of urea and is configured to receive exhaust. When the device is place in an SCR system, the downstream face of the hydrolysis catalyst 342 is configured such that exhaust exits the downstream face. FIG. 4D illustrates a catalytic device that is parallelogram-shaped in cross-section and includes a separate pyrolysis catalyst 352 that is triangle-shaped in cross-section and a separate hydrolysis catalyst 354 that is triangle-shaped in cross-section. The pyrolysis catalyst 352 and the hydrolysis catalyst 354 are positioned adjacently where a downstream face 358 of the pyrolysis catalyst is adjacent to an upstream face 360 of the hydrolysis catalyst to form the catalytic device. When the device is placed in an SCR system, the upstream face of the pyrolysis catalyst 356 is configured to receive an aqueous solution of urea and is configured to receive exhaust. When the device is place in an SCR system, the downstream face of the hydrolysis catalyst 362 is configured such that exhaust exits the downstream face.

FIG. 5 provides a sectional view of a portion of one embodiment of an SCR system as disclosed herein. Exhaust enters and exits the system along an axial flow path 48. The system includes a catalytic device comprising a pyrolysis catalyst 150 having an upstream face 154 and a hydrolysis catalyst 154 having a downstream face 156. The pyrolysis catalyst 150 and the hydrolysis catalyst are parallelogram-shaped in cross-section. The upstream face of the pyrolysis catalyst is positioned at angle α relative to the axial flow, (where α is an angle of about 20-70 degrees, and preferably about 30-50 degrees). An aqueous urea solution is introduced into the system through an injector 160. The injector is positioned at angle β relative to the axial flow, (where β is an angle of about 20-70 degrees, and preferably about 30-50 degrees). The aqueous urea solution is deposited on the upstream face 154 of the pyrolysis catalyst 154. The exhaust passes through the pyrolysis catalyst and enters the hydrolysis catalyst, exiting the hydrolysis catalyst at the downstream face 156. The downstream face 156 of the hydrolysis catalyst is positioned at angle γ relative to the axial flow, (where γ is an angle of about 20-70 degrees, and preferably about 30-50 degrees). Angles α and γ may be the same or different. Where angles α and γ are the same, the catalytic device may be parallelogram-shaped in cross-section.

FIG. 6 provides a sectional view of a portion of another embodiment of an SCR system as disclosed herein. The SCR system of FIG. 6 is configured similarly to the SCR system of FIG. 5. However, in FIG. 6, the pyrolysis catalyst 170 and the hydrolysis catalyst 172 are triangle-shaped in cross-section.

FIG. 7 provides a perspective view of one embodiment of a catalytic device as disclosed herein. In FIG. 6, the pyrolysis catalyst 180 and the hydrolysis catalyst 182 have a tubular shape from a side view and may be formed by cutting a tubular-shaped material traversely at an angle. The pyrolysis catalyst 180 and the hydrolysis catalyst 182 may be positioned adjacently to form the catalytic device, where the downstream face of the pyrolysis catalyst 184 is positioned adjacent to the upstream face of the hydrolysis catalyst 186. The catalytic device thus formed may have a tubular shape and angled upstream and downstream faces.

In the foregoing description, certain terms have been used for brevity, clearness, and understanding. No unnecessary limitations are to be implied therefrom beyond the requirement of the prior art because such terms are used for descriptive purposes and are intended to be broadly construed. The different configurations, systems and method steps described herein may be used alone or in combination with other configurations, systems and method steps. It is to be expected that various equivalents, alternatives and modifications are possible.

Blackwell, Bryan E., Liu, Z. Gerald, Harinath, Arvind V., Prasad, Pradeep

Patent Priority Assignee Title
10272421, Jun 28 2015 Johnson Matthey Public Limited Company Catalytic wall-flow filter having a membrane
10975879, Jul 18 2018 THE CHARLES MACHINE WORKS, INC Centrifugal fan
11300025, Nov 06 2018 CUMMINS EMISSION SOLUTIONS INC Systems and methods for reducing reductant deposit formation in a decomposition reactor of an exhaust gas aftertreatment system for an internal combustion engine
11480189, Jul 18 2018 The Charles Machine Works, Inc. Centrifugal fan
11686320, Jul 18 2018 The Charles Machine Works, Inc. Centrifugal fan
8747788, Jan 25 2013 Caterpillar Inc. Aftertreatment module having angled catalyst bank
8920531, Feb 18 2010 CATECH INC Device for reducing soot particles and method for the same
9321008, Apr 21 2010 Heesung Catalysts Corporation Device for discharging exhaust gas from diesel engine, having ammonolysis module
Patent Priority Assignee Title
3656915,
4684393, Jun 11 1984 E I DU PONT DE NEMOURS AND COMPANY, WILMINGTON DELAWARE, A CORP OF DE Herbicidal thiophenesulfonamides
4723988, Jun 11 1984 E I DU PONT DE NEMOURS AND COMPANY Herbicidal thiophenesulfonamides
4929586, Jun 09 1988 W R GRACE & CO -CONN Catalysts for selective catalytic reduction DeNOx technology
5281403, Sep 27 1991 NOELL, INC A CORPORATION OF DELAWARE Method for converting urea to ammonia
5300270, Aug 20 1992 WEXFORD MANAGEMENT LLC Hot-side electrostatic precipitator
5308810, Dec 28 1992 Atlantic Richfield Company Method for treating contaminated catalyst
5310714, Jul 08 1992 Mobil Oil Corp. Synthesis of zeolite films bonded to substrates, structures and uses thereof
5316661, Jul 08 1992 Mobil Oil Corporation Processes for converting feedstock organic compounds
5370849, Oct 29 1992 Regents of the University of California, The Metal chelate process to remove pollutants from fluids
5374410, Jul 08 1992 Mobil Oil Corporation NOx abatement process
5441713, Apr 29 1988 Nalco Fuel Tech Hardness suppression in urea solutions
5540047, Oct 06 1993 Siemens Aktiengesellschaft Method for reducing the nitrogen oxide concentration in the exhaust of an internal combustion engine or of a firing system
5546004, Nov 04 1993 Prasendt Investments, LLC Sensor for determining the course of concentration of an adsorbent substance
5547650, Mar 24 1994 Regents of the University of California, The Process for removal of oxides of nitrogen
5601792, Feb 24 1992 Cleaning exhaust gases from combustion installations
5645756, Apr 29 1988 Nalco Fuel Tech Hardness suppression in urea solutions
5658545, Mar 29 1995 The Regents of California Metal regeneration of iron chelates in nitric oxide scrubbing
5711147, Aug 19 1996 Lawrence Livermore National Security LLC Plasma-assisted catalytic reduction system
5783428, Jul 19 1994 Mitsubishi Chemical Corporation Method of producing fumaric acid
5809774, Nov 19 1996 CLEAN DIESEL TECHNOLOGIES, INC System for fueling and feeding chemicals to internal combustion engines for NOx reduction
5827490, Sep 27 1991 Noell, Inc. Method for converting urea to ammonia
5849818, Jun 03 1993 Skin sulfonated particles in matrices
5886177, Jan 11 1994 ISIS Pharmaceuticals, Inc. Phosphate linked oligomers
5891409, Aug 19 1996 Lawrence Livermore National Security LLC Pre-converted nitric oxide gas in catalytic reduction system
5893267, Aug 19 1996 Lawrence Livermore National Security LLC Catalytic reduction system for oxygen-rich exhaust
6001922, Jan 31 1996 Eastman Chemical Comapny; Eastman Chemical Company Small particle size polyester/acrylic hybrid latexes
6038854, Aug 05 1997 Lawrence Livermore National Security LLC Plasma regenerated particulate trap and NOx reduction system
6093380, Oct 16 1998 Hera, LLC Method and apparatus for pollution control in exhaust gas streams from fossil fuel burning facilities
6120580, Apr 15 1998 IBIDEN CERAM ENVIRONMENTAL, INC ; CERAM ENVIRONMENTAL, INC Method for testing systems designed for NOx reduction in the combustion of carbonaceous fuels
6182443, Feb 09 1999 Ford Global Technologies, Inc. Method for converting exhaust gases from a diesel engine using nitrogen oxide absorbent
6187797, Dec 23 1996 Bristol-Myers Squibb Pharma Company Phenyl-isoxazoles as factor XA Inhibitors
6197268, Jul 02 1999 MESSER INDUSTRIES USA, INC Reduction of toxic substances in waste gas emissions
6203770, May 12 1997 Clean Diesel Technologies, Inc. Urea pyrolysis chamber and process for reducing lean-burn engine NOx emissions by selective catalytic reduction
6214195, Sep 14 1998 PPG Industries Ohio, Inc Method and device for transforming chemical compositions
6245134, Apr 15 1998 IBIDEN CERAM ENVIRONMENTAL, INC ; CERAM ENVIRONMENTAL, INC Apparatus for testing systems designed for NOx reduction in the combustion of carbonaceous fuels
6264905, Oct 12 1999 FUEL TECH, INC Method and apparatus for reducing "ammonia slip" in SCR and/or SNCR NOX removal applications
6267864, Sep 14 1998 PPG Industries Ohio, Inc Field assisted transformation of chemical and material compositions
6282371, Jul 02 1998 SELAS FLUID PROCESSING CORP Devices for reducing emissions, and methods for same
6311484, Feb 22 2000 Engelhard Corporation System for reducing NOx transient emission
6314722, Oct 06 1999 Matros Technologies, Inc. Method and apparatus for emission control
6361754, Mar 27 1997 CLEAN DIESEL TECHNOLOGIES, INC Reducing no emissions from an engine by on-demand generation of ammonia for selective catalytic reduction
6403620, Jun 18 1998 Bristol-Myers Squibb Pharma Company Inhibitors of factor Xa with a neutral P1 specificity group
6444006, May 18 2000 CUMMINS FILTRATION INC High temperature composite ceramic filter
6446430, Feb 22 2000 Engelhard Corporation System for reducing NOx transient emission
6449947, Oct 17 2001 CUMMINS FILTRATION INC Low pressure injection and turbulent mixing in selective catalytic reduction system
6455463, Mar 13 2001 Asec Manufacturing General Partnership; UMICORE AG & CO KG Alkaline earth/transition metal lean NOx catalyst
6468489, Aug 10 1999 Electric Power Research Institute, Inc. Apparatus and method for decreasing contaminants present in a gas stream
6475453, Feb 12 1996 JOHNSON MATTHEY CATALYSTS GERMANY GMBH Configuration for decomposing nitrogen oxides in a gas stream and method for using the configuration
6514742, Jul 29 1998 Daicel Chemical Industries, LTD D-aminoacylases, method for producing the same, and method for producing D-amino acids using the same
6517702, Nov 12 1999 Robert Bosch GmbH Sensor for the analysis of exhaust gases and analysis method
6531704, Sep 14 1998 PPG Industries Ohio, Inc Nanotechnology for engineering the performance of substances
6534022, Oct 15 1999 ABB LUMMUS GLOBAL, INC Conversion of nitrogen oxides in the presence of a catalyst supported on a mesh-like structure
6548512, Dec 23 1996 Bristol-Myers Squibb Pharma Company Nitrogen containing heteroaromatics as factor Xa inhibitors
6569874, Dec 23 1996 Bristol-Myers Squibb Pharma Company Thiazoles as factor Xa inhibitors
6581684, Apr 24 2000 Shell Oil Company In Situ thermal processing of a hydrocarbon containing formation to produce sulfur containing formation fluids
6582490, May 18 2000 CUMMINS FILTRATION INC Pre-form for exhaust aftertreatment control filter
6588503, Apr 24 2000 Shell Oil Company In Situ thermal processing of a coal formation to control product composition
6588504, Apr 24 2000 Shell Oil Company In situ thermal processing of a coal formation to produce nitrogen and/or sulfur containing formation fluids
6591906, Apr 24 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation with a selected oxygen content
6591907, Apr 24 2000 Shell Oil Company In situ thermal processing of a coal formation with a selected vitrinite reflectance
6601385, Oct 17 2001 CUMMINS FILTRATION INC Impactor for selective catalytic reduction system
6602895, Jun 19 1997 Bristol-Myers Squibb Company Inhibitors of factor Xa with a neutral P1 specificity group
6607033, Apr 24 2000 Shell Oil Company In Situ thermal processing of a coal formation to produce a condensate
6609570, Apr 24 2000 Shell Oil Company In situ thermal processing of a coal formation and ammonia production
6616901, Oct 16 1998 Hera, LLC Apparatus for pollution control in exhaust gas streams from fossil fuel burning facilities
6620393, Oct 12 1999 FUEL TECH, INC Method and apparatus for reducing "ammonia slip" in SCR and/or SNCR NOx removal applications
6624113, Mar 13 2001 Asec Manufacturing General Partnership; UMICORE AG & CO KG Alkali metal/alkaline earth lean NOx catalyst
6649347, Jun 23 2000 CHROMATIN, INC Use of methylated nucleic acid segments for isolating centromere DNA
6670296, Jan 11 2001 Asec Manufacturing General Partnership; UMICORE AG & CO KG Alumina/zeolite lean NOx catalyst
6688387, Apr 24 2000 SALAMANDER SOLUTIONS INC In situ thermal processing of a hydrocarbon containing formation to produce a hydrocarbon condensate
6698515, Apr 24 2000 Shell Oil Company In situ thermal processing of a coal formation using a relatively slow heating rate
6702016, Apr 24 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation with heat sources located at an edge of a formation layer
6708758, Apr 24 2000 Shell Oil Company In situ thermal processing of a coal formation leaving one or more selected unprocessed areas
6712135, Apr 24 2000 Shell Oil Company In situ thermal processing of a coal formation in reducing environment
6712136, Apr 24 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation using a selected production well spacing
6712137, Apr 24 2000 Shell Oil Company In situ thermal processing of a coal formation to pyrolyze a selected percentage of hydrocarbon material
6712869, Feb 27 2002 CUMMINS FILTRATION INC Exhaust aftertreatment device with flow diffuser
6713030, Apr 28 1998 Johnson Matthey Public Limited Company Process and apparatus for reducing the nitrogen oxide content in exhaust gases by the controlled addition of NH3
6715546, Apr 24 2000 Shell Oil Company In situ production of synthesis gas from a hydrocarbon containing formation through a heat source wellbore
6715547, Apr 24 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation to form a substantially uniform, high permeability formation
6715548, Apr 24 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation to produce nitrogen containing formation fluids
6715549, Apr 04 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation with a selected atomic oxygen to carbon ratio
6719047, Apr 24 2000 SALAMANDER SOLUTIONS INC In situ thermal processing of a hydrocarbon containing formation in a hydrogen-rich environment
6722123, Oct 17 2001 CUMMINS FILTRATION INC Exhaust aftertreatment device, including chemical mixing and acoustic effects
6722429, Apr 24 2000 SALAMANDER SOLUTIONS INC In situ thermal processing of a hydrocarbon containing formation leaving one or more selected unprocessed areas
6722430, Apr 24 2000 Shell Oil Company In situ thermal processing of a coal formation with a selected oxygen content and/or selected O/C ratio
6722431, Apr 24 2000 SALAMANDER SOLUTIONS INC In situ thermal processing of hydrocarbons within a relatively permeable formation
6725920, Apr 24 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation to convert a selected amount of total organic carbon into hydrocarbon products
6725921, Apr 24 2000 Shell Oil Company In situ thermal processing of a coal formation by controlling a pressure of the formation
6725928, Apr 24 2000 Shell Oil Company In situ thermal processing of a coal formation using a distributed combustor
6729395, Apr 24 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation with a selected ratio of heat sources to production wells
6729396, Apr 24 2000 Shell Oil Company In situ thermal processing of a coal formation to produce hydrocarbons having a selected carbon number range
6729397, Apr 24 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation with a selected vitrinite reflectance
6729401, Apr 24 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation and ammonia production
6732794, Apr 24 2000 SALAMANDER SOLUTIONS INC In situ thermal processing of a hydrocarbon containing formation to produce a mixture with a selected hydrogen content
6732795, Apr 24 2000 SALAMANDER SOLUTIONS INC In situ thermal processing of a hydrocarbon containing formation to pyrolyze a selected percentage of hydrocarbon material
6732796, Apr 24 2000 Shell Oil Company In situ production of synthesis gas from a hydrocarbon containing formation, the synthesis gas having a selected H2 to CO ratio
6736215, Apr 24 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation, in situ production of synthesis gas, and carbon dioxide sequestration
6739393, Apr 24 2000 Shell Oil Company In situ thermal processing of a coal formation and tuning production
6739394, Apr 24 2000 Shell Oil Company Production of synthesis gas from a hydrocarbon containing formation
6742587, Apr 24 2000 Shell Oil Company In situ thermal processing of a coal formation to form a substantially uniform, relatively high permeable formation
6742588, Apr 24 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation to produce formation fluids having a relatively low olefin content
6742589, Apr 24 2000 Shell Oil Company In situ thermal processing of a coal formation using repeating triangular patterns of heat sources
6742593, Apr 24 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation using heat transfer from a heat transfer fluid to heat the formation
6745831, Apr 24 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation by controlling a pressure of the formation
6745832, Apr 24 2000 SALAMANDER SOLUTIONS INC Situ thermal processing of a hydrocarbon containing formation to control product composition
6745837, Apr 24 2000 SALAMANDER SOLUTIONS INC In situ thermal processing of a hydrocarbon containing formation using a controlled heating rate
6749021, Apr 24 2000 Shell Oil Company In situ thermal processing of a coal formation using a controlled heating rate
6752210, Apr 24 2000 Shell Oil Company In situ thermal processing of a coal formation using heat sources positioned within open wellbores
6758268, Apr 24 2000 SALAMANDER SOLUTIONS INC In situ thermal processing of a hydrocarbon containing formation using a relatively slow heating rate
6761216, Apr 24 2000 Shell Oil Company In situ thermal processing of a coal formation to produce hydrocarbon fluids and synthesis gas
6763886, Apr 24 2000 Shell Oil Company In situ thermal processing of a coal formation with carbon dioxide sequestration
6769483, Apr 24 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation using conductor in conduit heat sources
6769485, Apr 24 2000 Shell Oil Company In situ production of synthesis gas from a coal formation through a heat source wellbore
6782947, Apr 24 2001 Shell Oil Company In situ thermal processing of a relatively impermeable formation to increase permeability of the formation
6789625, Apr 24 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation using exposed metal heat sources
6805195, Apr 24 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation to produce hydrocarbon fluids and synthesis gas
6820688, Apr 24 2000 Shell Oil Company In situ thermal processing of coal formation with a selected hydrogen content and/or selected H/C ratio
6826906, Aug 15 2000 Engelhard Corporation Exhaust system for enhanced reduction of nitrogen oxides and particulates from diesel engines
6833272, Jul 06 1999 Daimler AG Method and apparatus for determining the storage state of an ammonia-storing SCR catalyst
6835689, Oct 10 2000 Corning Incorporated NH3 generation catalysts for lean-burn and diesel applications
6855303, Jun 19 2003 National Technology & Engineering Solutions of Sandia, LLC Method for selective catalytic reduction of nitrogen oxides
6863874, Oct 12 1998 Johnson Matthey Public Limited Company Process and apparatus for treating combustion exhaust gas
6864213, Mar 13 2001 Asec Manufacturing General Partnership; UMICORE AG & CO KG Alkaline earth / rare earth lean NOx catalyst
6866097, Apr 24 2000 Shell Oil Company In situ thermal processing of a coal formation to increase a permeability/porosity of the formation
6871707, Apr 24 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation with carbon dioxide sequestration
6877554, Apr 24 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation using pressure and/or temperature control
6877555, Apr 24 2001 Shell Oil Company In situ thermal processing of an oil shale formation while inhibiting coking
6880633, Apr 24 2001 Shell Oil Company In situ thermal processing of an oil shale formation to produce a desired product
6880635, Apr 24 2000 Shell Oil Company In situ production of synthesis gas from a coal formation, the synthesis gas having a selected H2 to CO ratio
6888116, Apr 04 1997 Field concentrators for artificial dielectric systems and devices
6891138, Apr 04 1997 Electromagnetic susceptors with coatings for artificial dielectric systems and devices
6904752, Nov 30 2001 DELPHI TECHNOLOGIES IP LIMITED Engine cylinder deactivation to improve the performance of exhaust emission control systems
6905861, Jul 29 1998 Daicel Chemical Industries, Ltd. D-aminoacylases, method for producing the same, and method for producing D-amino acids using the same
6919047, Oct 10 2000 Corning Incorporated Reduction of nitrogen oxides in diesel exhaust gases and fuel injection system
6928807, Feb 14 2002 MAN Truck & Bus AG Method and apparatus for producing ammonia (NH3)
6946013, Oct 28 2002 Geo2 Technologies, Inc Ceramic exhaust filter
6946107, Oct 15 1999 ABB Lummus Global, Inc. Conversion of nitrogen oxides in the presence of a catalyst supported on a mesh-like structure
6972197, Mar 18 1999 CHROMATIN, INC Plant chromosome compositions and methods
6973967, Apr 24 2000 Shell Oil Company Situ thermal processing of a coal formation using pressure and/or temperature control
6979430, Dec 18 2002 Foster Wheeler Energy Corporation System and method for controlling NOx emissions from boilers combusting carbonaceous fuels without using external reagent
6981548, Apr 24 2001 Shell Oil Company In situ thermal recovery from a relatively permeable formation
6991031, Apr 24 2000 Shell Oil Company In situ thermal processing of a coal formation to convert a selected total organic carbon content into hydrocarbon products
6991032, Apr 24 2001 Shell Oil Company In situ thermal processing of an oil shale formation using a pattern of heat sources
6991033, Apr 24 2001 Shell Oil Company In situ thermal processing while controlling pressure in an oil shale formation
6991036, Apr 24 2001 Shell Oil Company Thermal processing of a relatively permeable formation
6991045, Oct 24 2001 Shell Oil Company Forming openings in a hydrocarbon containing formation using magnetic tracking
6994160, Apr 24 2000 SALAMANDER SOLUTIONS INC In situ thermal processing of a hydrocarbon containing formation to produce hydrocarbons having a selected carbon number range
6994161, Apr 24 2000 Shell Oil Company In situ thermal processing of a coal formation with a selected moisture content
6994168, Apr 24 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation with a selected hydrogen to carbon ratio
6996975, Jun 25 2004 Eaton Corporation Multistage reductant injection strategy for slipless, high efficiency selective catalytic reduction
6997255, Apr 24 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation in a reducing environment
7004247, Apr 24 2001 Shell Oil Company Conductor-in-conduit heat sources for in situ thermal processing of an oil shale formation
7004251, Apr 24 2001 Shell Oil Company In situ thermal processing and remediation of an oil shale formation
7011154, Oct 24 2001 Shell Oil Company In situ recovery from a kerogen and liquid hydrocarbon containing formation
7013972, Apr 24 2001 Shell Oil Company In situ thermal processing of an oil shale formation using a natural distributed combustor
7017389, Apr 20 2002 SUNY AT STONY BROOK, RESEARCH FOUNDATION OF, THE Sensors including metal oxides selective for specific gases and methods for preparing same
7017661, Apr 24 2000 Shell Oil Company Production of synthesis gas from a coal formation
7032660, Apr 24 2001 Shell Oil Company In situ thermal processing and inhibiting migration of fluids into or out of an in situ oil shale formation
7036583, Apr 24 2000 Shell Oil Company In situ thermal processing of a hydrocarbon containing formation to increase a porosity of the formation
7040084, Dec 16 2002 GM Global Technology Operations LLC Exhaust emission aftertreatment
7040397, Apr 24 2001 Shell Oil Company Thermal processing of an oil shale formation to increase permeability of the formation
7040398, Apr 24 2001 Shell Oil Company In situ thermal processing of a relatively permeable formation in a reducing environment
7040399, Apr 24 2001 Shell Oil Company In situ thermal processing of an oil shale formation using a controlled heating rate
7040400, Apr 24 2001 Shell Oil Company In situ thermal processing of a relatively impermeable formation using an open wellbore
7051807, Apr 24 2001 Shell Oil Company In situ thermal recovery from a relatively permeable formation with quality control
7051808, Oct 24 2001 Shell Oil Company Seismic monitoring of in situ conversion in a hydrocarbon containing formation
7051811, Apr 24 2001 Shell Oil Company In situ thermal processing through an open wellbore in an oil shale formation
7052532, Mar 09 2000 CUMMINS FILTRATION INC High temperature nanofilter, system and method
7055600, Apr 24 2001 Shell Oil Company In situ thermal recovery from a relatively permeable formation with controlled production rate
7060444, Sep 13 2002 Curagen Corporation Zone 3 necrosis associated markers and method of use thereof
7060458, Aug 14 1997 Wyeth Nucleic acid and amino acid sequences relating to Staphylococcus epidermidis for diagnostics and therapeutics
7065958, May 07 2002 EXTENGINE SYSTEMS, INC Emission control system
7127884, Nov 27 2003 PUREM GMBH, FORMERLY, EBERSPÄCHER EXHAUST TECHNOLOGY GMBH Muffler with an integrated catalytic converter
7240484, Dec 29 2003 Delphi Technologies, Inc. Exhaust treatment systems and methods for using the same
7328572, Feb 23 2006 CUMMINS FILTRATION INC Exhaust aftertreatment device with star-plugged turbulator
7533522, Sep 02 2005 EMITEC Gesellschaft fuer Emissionstechnologie mbH Method and apparatus for adding a reactant to an exhaust gas from an internal combustion engine
7814745, Jul 17 2007 Ford Global Technologies, LLC Approach for delivering a liquid reductant into an exhaust flow of a fuel burning engine
20060115402,
20070051097,
20080041040,
20090151334,
EP1481719,
WO9736676,
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